2021
DOI: 10.1016/j.scitotenv.2021.148781
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Formation of oil-particle aggregates: Impacts of mixing energy and duration

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Cited by 21 publications
(44 citation statements)
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“…The flasks were then sealed and placed in an orbital shaker (Thermo Scientific MaxQ 2000, MA, US) at 200 rpm, thus providing a flask-averaged energy dissipation rate (ε) of 0.5 W/kg. 46 Such a mixing energy is comparable to other experimental work 53,54 and was found to be the dominant mechanism for OPA formation as discussed in Ji et al 47 Table 1 lists the experiments conducted at different mixing durations, whereby the flasks mixed for a short period (i.e., 0.5 to 24 h) were prepared in a series of four and were only used to investigate OPA breakup and formation, while the ones mixed for longer periods (96 to 672 h) were prepared in a series of seven, of which three were used for analyzing the biodegradation of petroleum hydrocarbons and four were used to investigate OPA breakup and formation. In addition, two sets of control flasks were prepared, in triplicate, to investigate the biodegradation and evaporation of crude oil while subject to the same conditions without adding sediments.…”
Section: Methodssupporting
confidence: 88%
“…The flasks were then sealed and placed in an orbital shaker (Thermo Scientific MaxQ 2000, MA, US) at 200 rpm, thus providing a flask-averaged energy dissipation rate (ε) of 0.5 W/kg. 46 Such a mixing energy is comparable to other experimental work 53,54 and was found to be the dominant mechanism for OPA formation as discussed in Ji et al 47 Table 1 lists the experiments conducted at different mixing durations, whereby the flasks mixed for a short period (i.e., 0.5 to 24 h) were prepared in a series of four and were only used to investigate OPA breakup and formation, while the ones mixed for longer periods (96 to 672 h) were prepared in a series of seven, of which three were used for analyzing the biodegradation of petroleum hydrocarbons and four were used to investigate OPA breakup and formation. In addition, two sets of control flasks were prepared, in triplicate, to investigate the biodegradation and evaporation of crude oil while subject to the same conditions without adding sediments.…”
Section: Methodssupporting
confidence: 88%
“…Bubbles produced by breaking waves are also found in offshore areas . More importantly, the shoreline is not only a sink for pollutants but also plays host to further transport and transformation of pollutants. As a traditional pollutant in the ocean, oil spills seriously harm local ecosystems once stranded in the shoreline environment. , There have been many studies investigating the fate and transport of oil stranded on shorelines, but almost all have paid attention to only light irradiation, temperature, salinity, shoreline substrate, microbial degradation, and other conventional factors. NBs affect not only the physical transport of pollutants but also their chemical weathering, biodegradation, and adsorption with other environmental pollutants. Meanwhile, no studies have thus far focused on the potential effects of NBs on spilled oil in the shoreline environment.…”
Section: Introductionmentioning
confidence: 99%
“…As the oil‐particle aggregation proceeded, the aggregated oil may be stretched due to the continuous adhesion of particles, further distorting the droplet surface. Additionally, formed OPAs may be more prone to break up over time, making the trapped oil droplets elongated (Ji et al., 2021). The oil type slightly affected the mean size and shape of trapped oil droplets, which supports the findings of Delvigne and Sweeney (1988) that the mean size of oil droplets is proportional to the oil kinematic viscosity.…”
Section: Discussionmentioning
confidence: 99%